EP1829853B1

EP1829853B1 - Biodiesel cold filtration process

Info

Publication number: EP1829853B1
Application number: EP07250435A
Authority: EP
Inventors: Myron Francis Renewable Energy Group Danzer; Timothy L. Renewable Energy Group Ely; Scott Alan Renewable Energy Group Kirgery; John Renewable Energy Group Mostek; Matthew L. Renewable Energy Group Schultes; Wayne Crown Iron Works Co. McCalley; William Crown Iron Works Co. McDonald
Original assignee: Crown Iron Works Co; Renewable Energy Group Inc
Current assignee: Crown Iron Works Co; Renewable Energy Group Inc
Priority date: 2006-02-02
Filing date: 2007-02-02
Publication date: 2009-04-15
Anticipated expiration: 2027-02-02
Also published as: DE602007000878D1; CN101029251A; US20150329791A1; MX2007001391A; US9109170B2; BRPI0705912A; CA2576750C; MY142979A; EP1829853A2; CA2576750A1; AR059305A1; CN101029251B; ATE428682T1; EP1829853A3; US11326115B2; ES2325796T3; US20070175091A1

Description

FIELD OF THE INVENTION

The invention relates to an improved process for producing biodiesel fuel. More particularly, the quality of the biodiesel fuel is improved by using a clod filtration process to remove non-methyl ester impurities and other contaminants, such as sterol glycosides and other unsaponifiables.

BACKGROUND OF THE INVENTION

There is significant interest in alternative fuels which are non-petroleum based for many reasons, including environmental, economic, political, and other reasons. Biodiesel fuel is one alternative based upon renewable resources. Biodiesel is a mono-alkyl ester of long chain fatty acids, such as methyl ester derived from fats and oils, and provides lower emissions as compared to petroleum-bases diesel fuel. The cetane number, energy content, viscosity, and phase changes of biodiesel are similar to petroleum diesel.
Biodiesel is derived from a transesterification chemical process wherein the triglyceride feedstock, such as fat or vegetable oil, is processes for conversion into methyl ester (biodiesel) and glycerine.
The American Society for Testing Materials (ASTM) has developed standards for biodiesel fuels, with the most common being D-6751. ASTM standard D-6751 sets commercial quality specifications required for biodiesel fuel. The D-6751 standard requires water and sediment be less than 0.050%, by volume, as measured by ASTM standard D-2709. However, biodiesel which meets the D-6751 ASTM standard can still contain contaminants which tend to crystallize and/or form and drop out solutions as sediment. When such biodiesels are used at lower temperatures, the precipitates create problems by decreasing the fuel flow and by clogging fuel lines, filters, and other components of the engines burning the fuel.
WO2005//037969 discloses a method of purifying a biodiesel fuel comprising contacting the biodiesel with at least one adsorbent material, such as magnesium silicate.
Therefore, a primary objective of the present invention is the provision of a process for producing biodiesel which eliminates or minimizes the precipitation problems of this alternative fuel.
Another objective of the present invention is the provision of an improved biodiesel production process which utilizes cold filtration for removing impurities and contaminants from the biodiesel.
Still another objective of the present invention is the provision of a method for improving the quality of biodiesel by removing particulates there from prior to storage or transportation.
Yet another objective of the present invention is the provision of a process for cooling and filtering biodiesel for the removal of formed sediments.
Another objective of the present invention is the provision of an improved biodiesel production process which removes non-methyl esters and glycosides from the biodiesel.
Still another objective of the present invention is a method of producing biodiesel by cooling the biodiesel with one or more heat exchangers which can be quickly and easily cleaned.
These and other objectives will become apparent from the following description of the invention.

BRIEF SUMMARY OF THE INVENTION

According to the present invention there is provided a method for removing impurities from biodiesel, comprising; converting a feedstock into biodiesel having temperature exceeding 98° C; cooling the biodiesel to a temperature of less than about 38°C to form particulates of impurities; and filtering the cooled biodiesel to remove the particulates.
The improved biodiesel production process of the present invention uses cold filtration to remove impurities and contaminants from the biodiesel. After the triglyceride feedstock is processed for separation into methyl esters and glycerine, the methyl ester biodiesel is cooled to a temperature of less than about 38°C (100°F) so that the impurities and contaminants precipitate out as particulars in the biodiesel liquid. Diatomaceous earth or other filtering material is then added to the cooled biodiesel to form a slurry, which is then filtered through a pressure leaf or other type of filter to remove the particulates. The filtered biodiesel is then run through a polish filter to remove any remaining sediments and diatomaceous earth, so as to produce the final biodiesel product.

BRIEF DESCRIPTION OF THE DRAWINGS

Figure 1 is a schematic view showing a preferred embodiment of the biodiesel production process according to the present invention.
Figure 2 is a schematic view showing a preferred embodiment of the cold filtration step in the biodiesel production process of the present invention.

DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENT

Figure 1 shows a preferred process for producing improved quality biodiesel, including the novel cold filtration step of the present invention. The process includes five general steps, including the pretreatment step 10, the biodiesel production step 12, the cold filtration step 14, the optional winterization step 16, and the optional fractionation step 18. The pretreatment step 10, biodiesel production step 12, and winterization and fractionation steps 16, 18 are known in the industry. The improved quality biodiesel is a result of the cold filtration step 14.
The purpose of the pretreatment step 10 is to remove contaminants and impurities, such as phospholipid gums and free fatty acids, from the triglyceride feedstock, so as to clean up the feedstock in preparation for the biodiesel production step 12. Conventional technology is used in this pretreatment step 10, such as degumming, caustic refining, and silica adsorbent filtration.
The biodiesel production step 12 converts the triglycerides into methyl esters (also known as biodiesel) and glycerin. The conventional technology for this production step 12 utilizes transesterification reaction with methanol in the presence of a sodium methoxide catalyst so as to separate the methyl esters from the glycerin.
The winterization step 16 is optional, depending upon the climate in which the biodiesel is to be used. The purpose of winterization is to improve the cold flow and winter performance of the fuel. The winterization step 16 removes saturated methyl esters, such as C16:0 methyl palmitate and C18:0 methyl sterate, though such removal is indiscriminate. The winterization technology is conventional, and utilizes the crystallization of saturates by controlling the time, temperature and agitation of the biodiesel. The crystals are then removed by decantation and filtration.
The fractionation step 18 is also optional, depending upon the temperatures in which the biodiesel is to be used. Fractionation improves the cold flow and winter performance of the fuel, by selectively separating methyl esters into individual components or fractions. Conventional fractionation technology is utilized, including urea fractionation, solvent fractionation, or thermal distillation.
The biodiesel production process of the present invention improves the quality of the biodiesel by adding the novel cold filtration step 14. The purpose of the cold filtration step 14 is to clean up the biodiesel fuel by removing trace contaminants, including sterol glycosides and other unsaponifiables which are naturally present, as well as non-methyl ester impurities. The cold filtration step 14 generally involves cooling the biodiesel to at least about 70°F (about 21°C), adding diatomaceous earth or other adsorbent to the biodiesel to form a slurry, and filtering the slurry through a pressure leaf or other type of filter to remove solids formed during the cooling of the biodiesel.
The cold filtration step 14 is shown in greater detail in Figure 2. The biodiesel 20 resulting from the production step 12 is first cooled through one or more stages 22, as indicated by arrow A. Any conventional cooling systems can be utilized, such as heat exchangers 24. Typically, the biodiesel produced by the production step 12 is approximately 290°F (143°C), or more. At the end of the cooling stage or stages 22, the temperature is preferably between about 40-100°F (4-38°C), with about 65-80°F (18-27°C) being preferred, with a most preferred temperature of approximately 70°F (22°C). For example, in one embodiment, an economizer is used in a first cooling stage so as to reduce the temperature of the biodiesel product from approximately 290°F (143°C) down to approximately 200-220°F (93-105°C), with about 210°F (99°C) being preferred, by transferring heat into a stripper feed stream. In a second cooling stage, a cooling water exchanger is used to further reduce the temperature of the biodiesel product 20 from approximately 210°F (99°C) down to approximately 80-90°F (26-33°C), with about 85°F (30°C) being preferred, by transferring heat into a cooling water recirculation loop. In a third cooling stage, a chilled fluid exchanger is used to further reduce the temperature of the biodiesel product 20 from approximately 85°F (30°C) down to approximately 65-75°F (about 18-24°C), with about 70°F (22°C) being preferred, by transferring heat into a chilled fluid recirculation loop, such as a solution of glycol and water. The minimum final cooled temperature should be no less than 40°F (4°C), such that the natural saturated fats of the oil do not crystallize.
At the conclusion of the cooling stage(s) 22, cooled biodiesel product is sent to a filter feed surge tank 26, as indicated by arrow B, for a sufficient time to allow the impurities and contaminants to solidify and precipitate in the form of particulates. Typically, the residence time in tank 26 is approximately 1-1 ½hours. However, persons skilled in the art would readily appreciate that the biodiesel product may remain in the tank for shorter or longer periods of time depending upon a number of factors, including degree of impurities in the product, amount of product, degree of purity desired, convenience factors, etc. Depending upon the volume of the tank 26, the tank may be insulated or refrigerated to maintain the temperature of the biodiesel product.
After the sediments have formed in the biodiesel, the biodiesel product is transferred to a body feed tank 28, as represented by arrow C, wherein a filter aid from a feeder 30 is added to the biodiesel (arrow D), with about 0.1-0.25% by weight filter aid being preferred. Persons skilled in the art would readily understand that more or less filter aid may be added based on a number of factors, including source of feedstock, degree of filtration desired, convenience, cost, etc. One preferred filter aid is diatomaceous earth. Diatomaceous earth is characterized by high porosity, in that up to 85% of the volume of diatomaceous earth is made up of tiny inner connected pores and voids. Thus, diatomaceous earth has a high adsorption capacity, up to 100% of its weight in liquid, while still exhibiting properties of a dry powder. An agitator may be provided in the tank 28 to facilitate the mixing of the biodiesel, sediments, and diatomaceous earth into a slurry. Other conventional filtration materials may also be used instead of or in addition to the diatomaceous earth in this step, including sand, silica, or other finely graded materials. Such filtration materials are well known to persons skilled in the art, and include silica (of various grade sizes, and either inert or chemically activated), clay (such as acid-activated bleaching clay), cellulose, mined and milled volcanic deposits, minerals of all types (including perlite), and magnesium silicate (such a Magnesol sold by the Dallas Group). Entrained biodiesel mist in the tank 28 may be removed by a demister 32 (arrow E) which is connected to an external vent 34 (arrow F). Such mist droplets mat be present in the air vapour exhaust which is vented during the filter blow-down and cake drying steps ( described below), and preferably is removed via the demister 32 or other conventional means.
The biodiesel slurry is then piped to the filter 36 (arrows G and H) for removal of the particulates. Preferably, the filter 36 is a pressure leaf filter whose mesh screens have preferably been precoated with a similar media as that used in the filtration step. Other types of suitable filters for this step include, but are pilot limited to, pressure filters such as tube or candle fillers, horizontal pressure filters, or filter presses. The diatomaceous earth or other filtration material previously added to the bulk biodiesel acts as a body feed that allows for the buildup of a filter cake on the leaves of the filter36, thereby effectively removing the sediment in the biodiesel at the sub-micron level, while allowing the liquid biodiesel to pass through the cake with minimal pressure drop. With a body feed addition of 0.1-25% diatomaceous earth by weight of biodiesel feed, for example, the filter 36 should be expected to run from 4 to 12 hours before cleaning is required. Cleaning of the filter 36 is accomplished using any convenient method known in the industry. Other filtration equipment using different types of media may also be utilized, such as carbon, activated charcoal, cloth or fabric (made of natural or synthetic materials), and ion exchange resin beads.
After the biodiesel product passes through the filter 36, quality mat be tested. If the quality is insufficient, the product can be redirected to the tank 28, as indicated by arrow 1, with further mixing with filtration material from the feeder 30 and further filtering through the filter 36.
In one series of preliminary tests utilizing 0.2% or less, by weight, of diatomaceous earth with biodiesel at a temperature cooled to at least 100°F (38°C), the pressure leaf filter 36 reduced water and sediment from the biodiesel product to less than 0.01% by weight. The tests imply, and conservatively support utilization of diatomaceous earth feed rate of about 186.6 grams/minute, with biodiesel feed rate approximately 554 pounds/minute (251.3kg/minute) to the filter 36 (i.e., about 0.019% diatomaceous earth body feed).
An initial filtration run was conducted for about 6 hours at the rate of 540 pounds/minute (245 kg/minute) so as to result in approximately 197,000 pounds (89359.2 kg) of biodiesel product being fed to the filtration assembly 36. Sediment and /or floaters for this period were noted as being absent together. Pressure loss across the filtration assembly 36 was noted at about 0.8 psi. After shutdown of the vertical leaf filter 36, draining, and 3 - minute blown down, samples were obtained, with outstanding tests for the residual biodiesel oil, however, the "cake" was characterized as "dry".
Clean biodiesel product exiting the filter 36, and which does not need to be refiltered via line 1, is then directed to a filtrate surge tank 38, as indicated by arrow J. Tank 38 is optional and provides for production control. The clean biodiesel is then directed to a final product filter 40, as indicated by arrow K. In one embodiment, the filter 40 may be sock filters, which remove any final particulates, including diatomaceous earth, in the biodiesel product. The final step polishes the biodiesel to final clarity and removes any residual diatomaceous earth of filter cake that any have passed through the mesh screens of the filter 36. The polished biodiesel is sent to the appropriate storage tank 42 (arrow L) for certification and shipping.
Periodically, the leaf filter 36 must be cleaned. Cleaning or changing the pressure leaf filter 36 consists of taking the filter off-line, removing the liquid from the vessel, blowing the filter cake dry with air or nitrogen from a source 37 to minimize the loss of biodiesel product in the spent filter cake, and then discharging the dry filter cake from the screens. The filter 36 should be cleaned after a pre-set period of time, and when excessive pressure drop across the filter is noted during the operation. After cleaning, the filter36 must be recharged with filtration material on the mesh leaves. Such recharging can be accomplished by circulating the biodiesel/ filtration material slurry from the precoat feeder 44 which supplies filtration material to a biodiesel precoat tank 46, as indicated by arrow M. The slurry in the precoat tank 46 is then circulated through the leaf filter 36, as indicated by arrows P, H and O until the filter leaves are sufficiently coated. Then, the normal filtration of the biodiesel from the body feed tank 28 may continue. The slurry in the precoat tank 46 may also be vented through the demister 32, (discussed above) as indicated by arrow N.
The leaf filter pressure depends on numerous factors, such as equipment size, piping and flow parameters, and should be set according to ther manufacturer's design specification. A pressure relief line (arrow Q) is provided to divert biodiesel from the leaf filter 36 back to the body feed tank 28 in the event of over pressure.
Periodically, the heat exchangers 24 need cleaning. In other industrial applications of heat exchangers, multiple heat exchangers have been used so that the cooling process may continue during the cleaning operation by shutting down the one heat exchanger while using the other heat exchanger. In the present invention, cleaning of the heat exchangers 24 does not require a shut down of one exchanger for cleaning while the other heat exchangers operate. Rather, cleaning is quickly and easily accomplished using a clean-in-place procedure by shutting off the flow of cooling fluid for a short period of time to the heat exchangers, while continuing to run the hot biodiesel product 20 through the heat exchangers, and then recycling the hot biodiesel through a recycle line 48, as indicated by arrows R and S. By running the hot biodiesel through the heat exchangers without cooling, any sediment buildup in the exchangers is dissolved in approximately one minute, or less, and thereby returns to suspension in the biodiesel product. After the exchangers 24 are cleaned, the coolant flow is restored to the exchangers 24 for the continued cooling of the biodiesel product 20, as described above.
It is understood that the various lines shown in Figure 2 include valves and gauges for controlling and monitoring the flow of biodiesel during the cold filtration step 14.
The filtered and cleaned biodiesel may be tested to determine its quality, though such testing is not a required step in the cold filtration process.
One test method used to qualitatively determine filtration effectiveness and remaining sediment level in the finished product is to replicate the problematic storage and transportation conditions. This is achieved in the lab by cooling a 100 mL sample to 40°F (4°C) for 16 hours, then centrifuging the sample (per ASTM D-2709 test method) while still cold and visually inspecting the presence of sediment. The target product quality will have no visible sediment resulting from this test method. Alternatively, a sample can be allowed to freeze completely by subjecting it to 30°F (-1°C) or colder for 48 hours or more, then allowed to return to room temperature (approx. 75°F or 24°C). The sample is centrifuged as before and visually inspected for sediment. In all cases, the final product should be bright and clear with no visible sediment.
A far more formalized test method was implemented in the State of Minnesota to "determine the mass of particular contamination in a biodiesel fuel by filtration". This test method is a modified version of ASTM D-6217 and involves a cold soak of a 300 milliliter sample to 40°F (4°C) for 16 hours, followed by a natural warming to ambient temperature (70°F or 21°C), prior to filtering through a special lab apparatus. Technical staff on the National Biodiesel Board facilitated the modifications of this test method. All biodiesel fuel sold in Minnesota must pass this test with a filtration time of less than 360 seconds per the requirements of specific customers. Experience will this test has shown that the specification limits may not be adequate in identifying or preventing potential field problems, as either filtered or unfiltered fuels have easily passed the test.
Experience suggests the type and quality of the feedstock oil that is used to produce the biodiesel has an impact in the quality and nature of sediment formed. Biodiesel made from refined and bleached soybean oil tends to form sediment more readily when exposed to instantaneous cooling. Biodiesel made from less processed soybean oil (such as degummed or deodorized) tends to require prolonged exposure to cooling temperatures before sediment will form. This time and temperature dependency on sediment formation could result in different field experience with unfiltered fuel. However, it is noted that regardless of the feedstock oil used, the cold filtration process described above is successful at removing sediment- forming materials.

Claims

A method for removing impurities from biodiesel, comprising; converting a feedstock into biodiesel having a temperature exceeding 98°C; cooling the biodiesel to a temperature of less than 38°C to form particulates of impurities; and filtering the cooling biodiesel to remove the particulates.
The method of claim 1 whereby the biodiesel is cooled to a temperature between 4-38°C.
The method of claim 1 wherein the cooling step is preformed in multiple stages using a of exchangers.
The method of claim 3 further comprising periodically cleaning the heat exchangers by running un-cooled fluid to the exchangers.
The method of claim 3 wherein a first cooling stage reduces the biodiesel temperature to 93-105°C, and a second cooling stage reduces the biodiesel temperature to 26-33°C, and a third cooling stage further reduces the biodiesel temperature to at least 18-24°C.
The method of claim 1 wherein the filtering step includes multiple stages.
The method of claim 6 wherein a first filtering stage includes the addition of an absorbent to the biodiesel.
The method of claim 7 whereby the absorbent is selected from the group; consisting of diatomaceous earth, silica, sand, and mixtures thereof.
The method of claim 8 wherein the absorbent is diatomaceous earth.
The method of claim 9 wherein the diatomaceous earth is between 0.1% to 0.25% by weight of the biodiesel.
The method of claim 7 wherein the first filtration stage includes a leaf filter.
The method of claim 6 wherein a second filtration state includes a sock filter.
The method of claim 1 wherein the feedstock includes triglycerides and the biodiesel includes methyl esters, the method further comprising; pretreating the triglycerides to remove impurities.
The method of claim 13 further comprising adding an adsorbent to the methyl esters after cooling and before filtering to form a slurry.
The method of claim 14 wherein the adsorbent is diatomaceous.
The method of claim 14 wherein the slurry is filtered through a leaf filter to remove particles from the biodiesel.
The method of claim 13 further comprising winterizing the filtered methyl esters.
The method of claim 17 further comprising fractionating the winterized methyl esters.
The method of claim 13 wherein the methyl esters meet ASTM D6751 specifications or greater before cooling.
The method of claim 4 further comprising restoring cooling fluid flow to the heat exchangers after the cleaning step and recycling the biodiesel used for cleaning to the heat exchangers for cooling.
The process of claim 20 further comprising adding an adsorbent to the cooled biodiesel prior to filtration.
The process of claim 21 wherein the adsorbent is diatomaceous earth.